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Spatial modelling of organic carbon in burned mountain soils using hyperspectral images, field datasets, and NIR spectroscopy (Cantabrian Range; NW Spain)

dc.contributor.authorFernández Menéndez, Susana del Carmen 
dc.contributor.authorPeón García, Juan José 
dc.contributor.authorRecondo González, María del Carmen 
dc.contributor.authorFernández Calleja, Javier Jesús 
dc.contributor.authorGuerrero, César
dc.date.accessioned2016-07-12T07:35:08Z
dc.date.available2016-07-12T07:35:08Z
dc.date.issued2016-07
dc.identifier.citationLand Degradation & Developmen, 27(5), p. 1479–1488 (2016); doi:10.1002/ldr.2452
dc.identifier.issn1099-145X
dc.identifier.urihttp://hdl.handle.net/10651/38331
dc.description.abstractSoil organic matter is seriously affected by fires and suffers changes in stock, composition, and distribution. In the North-West side of the Cantabrian Range (northern Spain) fires are very common. In order to develop a cartographic technique to map areas with high carbon stocks caused by fire, we test a technique based on calibrated VIS-NIR soil organic carbon models and hyperspectral images. Total (TOC) and oxidizable carbon (OC) were measured in 89 soil samples. The samples were scanned with VIS-NIR spectrometer (400–2500 nm), and the spectra were resampled to the hyperspectral image channels. Spectroscopic models for TOC and OC were fitted (R2>0.81) using partial least squares regression (PLSR). The predictions were regionalized to the hyperspectral image and the results validated with a new soil population consisting of 12 Valeri plots collected in burned slopes of the study area under heather vegetation. In soil samples, TOC and OC values are highly correlated (R = 0.92), and the coefficients of the PLSR models have a similar pattern, which suggests similar organic components. Nevertheless, there are significant differences in the values of the regression coefficients, much higher in the TOC model except at 560 and 2054 nm that might be interpreted as labile carbon components, and at 1590 nm. At this wavelength the coefficient of TOC is positive and OC is negative, and it could be interpreted as hydrocarbons components present in the TOC model.eng
dc.description.sponsorshipThis work was funded by the Government of Asturias through the project SV-PA-13-ECOEMP-40. J. Peón acknowledges a PhD Grant from the University of Oviedo and a PhD Grant “Severo Ochoa” from the Government of Asturias (BP14-104). We also acknowledge INTA for providing the images and for the geometric and atmospheric correction.eng
dc.format.extentp. 1479-1488spa
dc.language.isospaspa
dc.relation.ispartofLand Degradation & Development, 27spa
dc.rights© 2015 John Wiley
dc.subjectTotal organic carbonspa
dc.subjectOxidizable organic carbonspa
dc.subjectSoil organic carbon mappingspa
dc.subjectVIS-NIR spectroscopyspa
dc.subjectHyperspectral remote sensingspa
dc.titleSpatial modelling of organic carbon in burned mountain soils using hyperspectral images, field datasets, and NIR spectroscopy (Cantabrian Range; NW Spain)eng
dc.typejournal articlespa
dc.identifier.doi10.1002/ldr.2452
dc.relation.projectIDSV-PA-13-ECOEMP-40spa
dc.relation.publisherversionhttp://dx.doi.org/10.1002/ldr.2452spa
dc.rights.accessRightsopen accessspa
dc.type.hasVersionAM


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